Carbon Nanotubes for adsorption of Organic contaminants

Carbon Nanotubes for Adsorption
of Organic Contaminants
By Dr. Shamsa Kanwal
CNTs
• Since the first discovery in 1991 (Iijima, 1991), CNTs
have attracted enormous research attention in various
scientific communities.
• Cylindrical nanostructure or Nanotubes have been
constructed with length-to-diameter ratio of up to
132,000,000:1, significantly larger than for any other
material.
• Nanotubes are categorized as single-walled nanotubes
(SWNTs) and multi-walled nanotubes (MWNTs).
Individual nanotubes naturally align themselves into
"ropes" held together by van der Waals forces, more
specifically, pi-stacking.
CNTs as adsorbents for removal of
organic and inorganic pollutants
• Adsorption is a simple and efficient method for the removal of
organic and inorganic compounds in drinking water treatment.
Among the various adsorbents, such as activated carbons
(ACs), zeolites, and resins, ACs are one of the most widely used
type of adsorbents in water treatment, because of their several
merits: broad-spectrum removal capability toward pollutants,
chemical inertness, and thermal stability.
• However, the application of ACs in water treatment also suffers
from several bottlenecks, such as slow adsorption kinetics and
difficulty for regeneration.
Continued….
• To overcome the above problems, activated carbon fibers
(ACFs) were developed as the second generation of
carbonaceous adsorbents.
• The pores in ACFs are directly opening on the surface of
carbon matrix, which shortens the diffusion distance of
pollutants to adsorption sites. As a result, ACFs usually
possess higher adsorption kinetics than ACs.
• CNTs, with one dimensional structure, like miniaturized
ACFs. All adsorption sites locate on the inner and outer
layer surface of CNTs. With the hollow and layered
structures and tunable surface chemistry, theoretically,
CNTs may be a promising third generation of carbonaceous
adsorbents.
Adsorption of Aromatic Compounds
on CNTs
• In most cases, several driving forces act simultaneously,
including hydrophobic effect, π-π interaction, π-π
electron-donor-acceptor (EDA) interaction,
electrostatic interaction, and hydrogen bonding.
Because of the hydrophobic nature of their outer
surfaces, CNTs have a strong affinity to organic
chemicals, especially to nonpolar organic compounds,
such as naphthalene , phenanthrene, and pyrene.
• Abundant π electrons on CNT surfaces enable a strong
π-π coupling of aromatic pollutants with the CNT
surface.
Continued…
• A common observation from these studies was that carbon
nanotubes are very strong adsorbents for hydrophobic
organic compounds. This is understandable considering the
strong hydrophobicity and high surface area of carbon
nanotubes. Additionally, an important implication from
several of the studies is that electronic polarizability of the
aromatic rings on the surface of carbon nanotubes might
considerably enhance adsorption of the organic
compounds to carbon nanotubes .
• For example, Long and Yang* found that, in the lowconcentration regime, the amount of dioxin adsorbed to
carbon nanotubes was much higher than that adsorbed to
activated carbon; they attributed it to the strong
interaction between the two benzene rings of dioxin and
the surface of the carbon nanotubes.
*Long, R. Q.; Yang, R. T. Carbon nanotubes as superior sorbent for dioxin removal. J. Am. Chem. Soc.
2001, 123, 2058–2059.
• The morphology of CNTs including nanoscale curvature and
chirality of graphene layers is expected to have a great
influence on the adsorption of organic pollutants, especially
for those with π-π stacking as the interaction force.
• Gotovac and coworkers observed remarkable difference
between the adsorption capacities of tetracene and
phenanthrene on the tube surface of CNTs because of the
nanoscale curvature effect. The morphology difference of
CNTs may also result in a difference in their aggregation
tendency, which may further impact their adsorption
ability. CNTs are prone to aggregation due to the strong van
der Waals forces along the length axis. The aggregation
tendency reduces with increased number of walls, or in
other words, reduced nanocurvature. Generally, the
aggregation of CNTs follows such an order: single-walled
CNTs (SWCNTs) > double-walled CNTs (DWCNTs) > multiwalled CNTs (MWCNTs)
*Gotovac S, Honda H, Hattori Y, Takahashi K, Kanoh H and Kaneko K, 2007a. Effect of nanoscale curvature of singlewalled carbon nanotubes on adsorption of polycyclic aromatic hydrocarbons. Nano Lett., 7(3): 583-587.
Figure 1. SWCNTs usually exist as bundles or ropes while
MWCNTs are randomly entangled as individual tubes. As a
consequence of aggregation, the available outer surface
was reduced while new adsorption sites appeared as
interstitial channels and grooves between the tubes in
CNT boundles.
Surface Chemistry Effects
• Surface chemistry is another important factor influencing the CNTs
adsorption behavior. Functional groups such as -OH, -C=O and -COOH
could be intentionally introduced onto CNT surfaces by acid oxidation or
air oxidation. Those functional groups make CNTs more hydrophilic and
suitable for the adsorption of relatively low molecular weight and polar
contaminants, such as phenol and 1,2-dichlorobenzene. Figure 2 is an
overview of the surface modification and effects of functional groups
on the adsorption properties of CNTs.
• The adsorption of heavy metals on CNTs depends mainly on the specific
complexation between metal ions and the hydrophilic functional groups
of CNTs (Rao et al., 2007). Therefore, without doubt, surface
functionalization of CNTs is favorable for the uptake of metal ions.
• Cho et al. (2010) reported that surface oxidation of CNTs enhanced the
adsorption of zinc and cadmium ions from aqueous solutions. T hey
found that the carboxyl-carbon sites of CNTs were over 20 times more
energetic for Zn(II) uptake than the unoxidized carbon sites.
*Rao G P, Lu C and Su F, 2007. Sorption of divalent metal ions from aqueous solution by carbon nanotubes: A review. Separation
and Purification Technology, 58(1): 224-231.
*Cho H H, Wepasnick K, Smith B A, Bangash F K, Fairbrother D H and Ball W P, 2010. Sorption of aqueous Zn[II] and Cd[II] by
multiwall carbon nanotubes: The relative roles of oxygen-containing functional groups and graphenic carbon. Langmuir, 26(2): 967981.
Fig. 2 Adsorption properties of CNTs as affected by the functional groups (Pan
and Xing, 2008).
• Another direct consequence of surface modification of CNTs with
hydrophilic groups is the improvement of CNT dispersion in aqueous
media.
• Rosenzweig et al. reported that the alcohol (OH) and acid (COOH)
moieties on CNTs can determine the aggregation state and accessible
sites for copper adsorption. The surface functionalized CNTs had higher
adsorption capacity for copper than pristine CNTs.
• It is worth noting that increasing the oxygen-containing functional
groups is a double-edged sword. It may have an adverse effect on the
adsorption of highly nonpolar chemicals like naphthalene (Cho et al.,
2008).
• Wu et al. (2012) systematically investigated the influence of surface
oxidation of MWCNT on the adsorption capacity and affinity of organic
compounds in water, and found that surface oxidation of MWCNTs
decreased the surface-area-normalized adsorption capacity of organic
compounds significantly because of the competition of water
molecules; meanwhile, the adsorption affinity of organic chemicals
were not altered because of the adsorption interactions (hydrophobic
effect, π-π interaction and hydrogen bond) remained constant.
*Rosenzweig S, Sorial G A, Sahle-Demessie E and Mack J, 2013. Effect of acid and alcohol network forces within functionalized multiwall
carbon nanotubes bundles on adsorption of copper (II) species. Chemosphere, 90(2): 395-402.
*Cho H H, Smith B A, Wnuk J D, Fairbrother D H and Ball W P, 2008. Influence of surface oxides on the adsorption of naphthalene onto
multiwalled carbon nanotubes. Environmental Science and Technology, 42(8): 2899-2905.
*Wu W H, Chen W, Lin D H and Yang K, 2012. Influence of surface oxidation of multiwalled carbon nanotubes on the adsorption affinity and
capacity of polar and nonpolar organic compounds in aqueous phase. Environmental Science and Technology, 46(10): 5446-5454.
In terms of adsorption kinetics…
the ordered pore structure of CNTs makes it easier for the diffusion of
pollutants to adsorption sites (Lu et al., 2005). This can be well
reflected through the comparison with ACs. ACs is usually rich in
micropores, which are sometimes not available for the access of
relatively large organic molecules.
Ji et al. (2009) investigated the adsorption of tetracycline to CNTs,
graphite and AC and found that the adsorption affinity of
tetracycline decreased in the order of graphite/SWNT > MWNT >>
AC upon normalization for adsorbent surface area. The weaker
adsorption of tetracycline to AC indicated that adsorption affinity
was greatly influenced by the accessibility of available adsorption
sites. The remarkably strong adsorption of tetracycline to CNTs can
be attributed to the strong adsorptive interactions (van der Waals
forces, π-π EDA interactions, cation-π bonding) with the graphene
surface of CNTs.
*Lu C S, Chung Y L and Chang K F, 2005. Adsorption of trihalomethanes from water with carbon nanotubes. Water Research, 39(6): 11831189.
*Ji L L, Chen W, Duan L and Zhu D Q, 2009. Mechanisms for strong adsorption of tetracycline to carbon nanotubes: A comparative study
using activated carbon and graphite as adsorbents. Environmental Science and Technology, 43(7): 2322-2327.
• Adsorption selectivity or resistance to harsh environment is an
important evaluation criterion for an adsorbent. A number of studies
have examined the importance of aqueous chemistry conditions on
the adsorption of SOCs by CNTs.
• Effects of solution pH and ionic strength on SOC adsorption by CNTs
are somewhat SOC-specific, the extent of which depends on the
ionizability and electron-donor-acceptor ability of the involved SOCs.
• The removal of Ni2+ and Zn2+ increased with solution pH in the range
of 1-8, reached maximum in the range of 8-11, and decreased as pH
over 12. The maximum adsorption in the pH range of 8-11 could be
attributed to the negatively charged surface functional groups of
CNTs and the formation of hydrated ion species such as M (OH)+1 and
M (OH)20.
• At a pH higher than 12, the predominant metal species was M(OH)31, and the heavy metal removal decreased due to the competition
between OH-1 and M(OH)3-1 and the repulsive force between the
negatively charged CNT surface and M(OH)3-1.
Adsorption of ionizable organic
compounds (IOCs)
• Many pesticides, antibiotics, and endocrine-disrupting
chemicals are ionizable in the environmentally relevant
pH range. Therefore, it is essential to fully understand
the forces that drive adsorption of ionizable organic
compounds (IOCs) from water to carbonaceous
substances including carbon nanotubes (CNTs),
activated carbon (AC), and natural and synthetic chars.
• These forces are important in the context of
environmental fate of IOCs, use of carbonaceous
materials as adsorbents in sensing and remediation of
IOCs, synthesis and use of derivatized CNTs in materials
and technological applications, and interactions of
carbonaceous substances released to the environment
with natural organic matter.
SNTs as sorbents
• With the number of aforementioned advantages: stronger chemical-nanotube
interactions, tailored surface chemistry, rapid equilibrium rates, and high
sorption capacity, CNTs were considered as superior sorbents for a wide range
of organic chemicals and inorganic contaminants than the conventional ACs.
However, for practical application in water treatment, the small particle size of
CNTs will cause excessive pressure drops and the recovery of spent CNTs is a
true challenge. The macroscopic manipulation of CNT monolithic blocks via
appropriate methods provide breakthrough for this bottleneck.
• Gui et al. (2010) made a monolithic CNT sponge by chemical vapor deposition
using ferrocene as precursor. The as-made CNT sponge had a randomly
intertwined three-dimensional structure and displayed high porosity and very
low density. The CNT sponge can float on oil-contaminated water and remove
oil with a large adsorption capacity (80 to 180 times their own weight for a
wide range of solvents and oils).
• The sponge had a tendency to move to the oil film area due to its high
hydrophobicity, leading to the unique “floating-and-cleaning” capability that is
very useful for spill cleanup.
*Gui X C, Wei J Q, Wang K L, Cao A Y, Zhu H W, Jia Y, Shu Q K and Wu D H, 2010. Carbon nanotube sponges. Advanced Materials, 22(5): 617-62
Application of CNT sponge in the cleanup of oil on water and densification of
cubic-shaped sponges into small pellets and full recovery to original structure
upon ethanol absorption (Gui et al., 2010)
CNTs as Scaffolds
• In addition to serving as direct adsorbents, CNTs can also be utilized as
excellent scaffold for macromolecules or metal oxides with intrinsic
adsorption ability. The tunable surface chemistry and controllable pore size
make CNTs good support for composite adsorbents.
• Examples of CNTs as scaffolds for pollutant removal include CNT decoration
with iron oxide for europium adsorption, chitosan for methyl orange
adsorption, (polyaniline for malachite green adsorption and ceria
nanoparticles for chromium adsorption.
• Maggini et al. (2013) synthesized a supermolecular adsorbent by coating
magnetic CNT with poly(vinylpyridine), which exhibited excellent removal
capacity of divalent metals from water, and the exhausted material can be
separated using magnetic field and regenerated by acid treatment. The
unique electrical properties of CNTs could be utilized for enhanced
adsorption with electrochemical assist.
• The mechanical flexibility and robustness, thermal stability and resistance to
harsh environment endow CNTs with excellent application potential in water
treatment. CNTs have the potential to serve as superior adsorbents for
removal of both organic and inorganic contaminants from water systems.
Nevertheless, there are several aspects that need to be evaluated prudently
before the real application in water treatment facilities, including cost,
reusability and the possibility of leakage into the environment.
• --------------------------------------*Maggini L, Raquez J M, Marega R, Ahrens J J, Pineux F, Meyer F, Dubois P and Bonifazi D, 2013. Magnetic poly(vinylpyridine)-coated
carbon nanotubes: An efficient supramolecular tool for wastewater purification. Chemsuschem, 6(2): 367-373.
Book Recommended
• Advances in Nanotechnology and the Environment by Juyoung Kim